Catalytic ozonation water treatment and impurity removal technology based on enhanced electron transfer efficiency
A technology for oxidizing water and electron migration, which is applied in the fields of oxidizing water/sewage treatment, water pollutants, water/sewage treatment, etc., which can solve the problem that the generation of toxic by-product bromate cannot be suppressed, and the toxic by-product of bromate cannot be effectively reduced. , the poor effect of advanced treatment of domestic sewage, etc., to achieve the effect of improving the reaction rate and mineralization capacity, shortening the degradation time, and ensuring the safety of water quality
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specific Embodiment approach 1
[0023] Specific embodiment one: the preparation method of perovskite type oxide / graphitic carbon nitride of the present embodiment is: (1) take by weighing 4.0mmol lanthanum nitrate, 4.0mmol cobalt nitrate, 8.0mmol citric acid, the amount of ion total substance The ratio of the concentration to the concentration of the citric acid substance is 1:1; (2) Dissolve the above chemicals in 15mL ethanol and 5mL distilled water to make a complex solution with a certain concentration, and stir at room temperature for 12h; (3) Dissolve the above The complex solution was heated and stirred at 90°C until it was evaporated to dryness, and then ground; (4) the dry powder obtained in step (3) was calcined at 750°C for 4 (heating rate 2°C / min) to obtain LaCoO 3 Solid powder; (5) with 1.5g urea, the LaCoO obtained in 0.5g step (4) 3 Add it into 10mL water and stir for 4h; (6) Dry the suspension obtained in step (5) at 90°C and grind it; (7) Dry the dry powder obtained in step (6) in a semi-clo...
specific Embodiment approach 2
[0024] Specific embodiment two: decontamination technology is realized according to the following steps in the catalytic ozonation system: (1) process required O 3Concentration is 1.0mg / L; (2) perovskite type oxide / graphitic carbon nitride dosage required by the process is 0.25g / L; (3) pollutant concentration in the water body to be treated is 10.0mg / L; ( 4) The concentration of bromide ions in the water to be treated is 100 μg / L; (5) The contact time is 120 minutes; (6) The pH range of the reaction system is 6.40.
[0025] Depend on figure 1 It can be seen that the effect of ozone oxidation degradation of benzotriazole alone is not good, and the efficiency of catalytic ozone oxidation degradation of benzotriazole is improved after adding perovskite oxide or graphite phase carbon nitride. Adding lanthanum cobaltate / graphite phase The efficiency of catalyzed ozone oxidation degradation of benzotriazole is significantly improved when the carbon nitride catalyst is used, and is ...
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